Toxicity of proton-metal mixtures in the field: linking stream macroinvertebrate species diversity to chemical speciation and bioavailability

Stockdale, Anthony; Tipping, Edward ORCID: https://orcid.org/0000-0001-6618-6512; Lofts, Stephen ORCID: https://orcid.org/0000-0002-3627-851X; Ormerod, Stephen J.; Clements, William H.; Blust, Ronny. 2010 Toxicity of proton-metal mixtures in the field: linking stream macroinvertebrate species diversity to chemical speciation and bioavailability. Aquatic Toxicology, 100 (1). 112-119. https://doi.org/10.1016/j.aquatox.2010.07.018

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Official URL: http://dx.doi.org/10.1016/j.aquatox.2010.07.018

Abstract/Summary

Understanding metal and proton toxicity under field conditions requires consideration of the complex nature of chemicals in mixtures. Here, we demonstrate a novel method that relates streamwater concentrations of cationic metallic species and protons to a field ecological index of biodiversity. The model WHAM-FTOX postulates that cation binding sites of aquatic macroinvertebrates can be represented by the functional groups of natural organic matter (humic acid), as described by the Windermere Humic Aqueous Model (WHAM6), and supporting field evidence is presented. We define a toxicity function (FTOX) by summing the products: (amount of invertebrate-bound cation)  (cation-specific toxicity coefficient, i). Species richness data for Ephemeroptera, Trichoptera and Plecoptera (EPT), are then described with a lower threshold of FTOX, below which all organisms are present and toxic effects are absent, and an upper threshold above which organisms are absent. Between the thresholds the number of species declines linearly with FTOX. We parameterised the model with chemistry and EPT data for low-order streamwaters affected by acid deposition and/or abandoned mines, representing a total of 412 sites across three continents. The fitting made use of quantile regression, to take into account reduced species richness caused by (unknown) factors other than cation toxicity. Parameters were derived for the four most common or abundant cations, with values of i following the sequence (increasing toxicity) H+ < Al < Zn < Cu. For waters affected mainly by H+ and Al, FTOX shows a steady decline with increasing pH, crossing the lower threshold near to pH 7. Competition effects among cations mean that toxicity due to Cu and Zn is rare at lower pH values, and occurs mostly between pH 6 and 8.

Item Type:	Publication - Article
Digital Object Identifier (DOI):	https://doi.org/10.1016/j.aquatox.2010.07.018
Programmes:	CEH Topics & Objectives 2009 - 2012 > Biogeochemistry > BGC Topic 3 - Managing Threats to Environment and Health > BGC - 3.2 - Provide the evidence base for setting Environment Quality Standards ...
UKCEH and CEH Sections/Science Areas:	Shore
ISSN:	0166-445X
Additional Keywords:	acidification, bioavailability, macroinvertebrates, metals, modelling, quantile regression, streamwaters, toxicity
NORA Subject Terms:	Ecology and Environment Chemistry
Date made live:	23 Sep 2010 09:22 +0 (UTC)
URI:	https://nora.nerc.ac.uk/id/eprint/10944

Item Type:

Publication - Article

Digital Object Identifier (DOI):

https://doi.org/10.1016/j.aquatox.2010.07.018

Programmes:

CEH Topics & Objectives 2009 - 2012 > Biogeochemistry > BGC Topic 3 - Managing Threats to Environment and Health > BGC - 3.2 - Provide the evidence base for setting Environment Quality Standards ...

UKCEH and CEH Sections/Science Areas:

Shore

ISSN:

0166-445X

Additional Keywords:

acidification, bioavailability, macroinvertebrates, metals, modelling, quantile regression, streamwaters, toxicity